Lecture 13 Flashcards

(31 cards)

1
Q

what are PFAS?

A
  • group of over 9000 synthetic chemicals that have been used in industry and consumer products for over 70 years
  • a group of organofluorine chemical compounds that have multiple fluorine atoms attached to an alkyl chain with a hydrophilic functional group
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2
Q

what are the characteristics of PFAS?

A
  • carbon-fluoride bond, one of the strongest bonds in organic chemistry
  • exhibit high resistance to degradation and heat, thus can be very persistent in the environment with degradation periods of years, decades, or longer
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3
Q

what are PFAS uses?

A

broad range of consumer products:
- food packaging
- nonstick cookware
- stain resistant fabrics and carpets
- some cosmetics
- firefighting foam

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4
Q

what were PFAS manufactured and when did they appear in the environment?

A
  • manufacturing began in the 1940s
  • first detection in wildlife was reported 50 years later
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5
Q

what do PFAS bind to?

A

proteins = proteinophilic

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6
Q

what are PFAS branded as?

A
  • forever chemicals
  • PFOS and PFOA are generally referred to as ‘legacy PFAS’
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7
Q

groups of PFAS include:

A
  • PASs
  • PFCAs
  • PFSAs
  • FTOH
  • PFAAs
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8
Q

what are physico-chemical characteristics of PFASs?

A
  • resistance to both environmental and biological degradation
  • thermal and chemical stability against oxidation, photolysis, and hydrolysis reactions
  • hydrophobicity
  • oleophobicity (resistant to the penetration of oils)
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9
Q

what is the relationship between PFASs and the stockholm convention?

A

3 PFASs have been listed under the stockholm convention:
- PFOA, its salts, and PFOA-related compounds = annex A
- PFOS, its salts, and POSF = annex B
- PFHxS, its salts, and PFHxS related compounds = annex A
- in 2021, long chain PFCAs and their precursors have also been proposed by the canadian government for inclusion in the stockholm convention

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10
Q

what are 3 exemptions under status B for PFOS?

A
  1. photo imaging
  2. aviation hydraulic fluids
  3. firefighting foam
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11
Q

what are unregulated PFASs?

A
  • GenX chemicals (a group used as substitutes for PFOA and PFOS)
  • FTOH
  • PFBS: a shorter chain PFAS (C>/= 6) used in various applications, remains unregulated for the most part
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12
Q

what are PFAS replacement products?

A

short-chain PFBSs:
- Technical performance is lower than that of long chain PFHxS and PFOS
- Much larger quantities of PFBS have thus been used to achieve a similar performance to PFHxS and PFOS
- Short-chain PFASs are highly mobile in the water bodies
- Final degradation products are extremely persistent
- A lack of regulations and proper water treatment techniques for short-chain alternates will bring about the never-ending existence of these contaminants in the aqueous environment

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13
Q

what are sources of PFAS to the marine environment?

A
  • PFAS production sites, such as chemical industries
  • Improper disposal practices, often originating from
    nonpoint sources and runoff from landfills
    containing PFAS
  • Inland activities (e.g., biosolids) are another
    significant contributor to PFAS pollution in marine ecosystem as they can introduce PFAS into the marine environment through riverine discharges
  • Volatile PFAS can be transported through the atmosphere, serving as another major source of PFAS contamination in marine and terrestrial
    environments
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14
Q

how are PFASs transported via atmospheric transport?

A
  • PFASs are known to undergo long-range transport to remote environments such as the Arctic via oceanic or atmospheric transport
  • Mechanism remains largely unknown
  • Neutral PFASs (e.g., FTOHs, FOSEs, FOSAs)
    are more volatile and less water soluble than PFAAs and are susceptible to long-range atmospheric transport to the Arctic
  • Neutral PFASs can be degraded in the atmosphere to form ionic PFAAs and
    subsequently deposit via wet or dry atmospheric deposition
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15
Q

how do PFAS partition?

A
  • Short-chain PFASs more dominant in
    the water and can form up to 88.8% of
    the total PFAS concentration in water
  • Long-chain PFASs more dominant in
    the sediment and SPM (suspended
    particulate matter)
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16
Q

what are the human health affects of PFASs?

A
  • Nearly all Canadians carry low levels of
    perfluorinated chemicals, including PFOS, in their blood as a result of exposure
  • ƩPFAS35 drinking water limit (Canada): 30 ng/L
  • ƩPFAS20drinking water limit (EU): 100 ng/L
  • PFOS and PFOA: 4 ng/L for each (USEPA)
  • Half-life in humans range from 2.3-7.3 years
  • Immunosuppression, neurological disorders, cancer
17
Q

how are PFASs directly vs. indirectly emitted into the environment?

A
  • directly: manufacture, use and disposal of products containing PFASs
  • indirectly: abiotic or biotic degradation of their precursors/ the production of persistent metabolites such as PFOS
18
Q

how do PFASs transport within an organism?

A
  • molecules enter the organism and reach various tissues through blood circulation
  • PFASs contain a terminal acidic group and a long highly hydrophobic carbon chain. due to their structural similarity to fatty acids, PFASs are able to competitively bind to various transport proteins
19
Q

what are the toxic effects of PFASs?

A
  • they are primarily mediated by their binding to proteins, nuclear receptors, and membranes
  • eg. PFASs can regulate PPAR signalling by binding to the classical ligand-binding pocket in the receptor or by interacting with its allosteric binding sites
20
Q

what are transport proteins?

A
  • play important roles in the distribution and accumulation of PFASs in the body
  • HSA is responsible for the transport of PFASs in blood circulation
  • L-FABP is responsible for the entry of PFASs into the liver
  • NTCP then carries PFASs from the liver to bile, from there PFASs are absorbed into the intestinal epithelial cells following the same mechanism as bile acids
21
Q

PFAS marine mammal tissue accumulation:

A
  • PFOS was first reported in tissues of 15 marine mammal species collected worldwide in 2001
  • highest concentrations of PFAS are found in the livers followed by kidneys in fish and marine mammals
22
Q

PFAS contamination in the arctic:

A
  • polar bears, the apex predator in arctic regions, have been found to be among the most contaminated wildlife
  • these chemicals cross the blood-brain barrier of bears, and inner regions of the brain contain high concentrations of PFASs
  • long chain PFCAs (C11-15) and PFOS was found to be predominant in the brain of bears
23
Q

PFAS contamination at the poles:

A
  • PFOS and long chained PFCAs (C9-12) have been detected in canadian arctic and greenland ringed seals
  • FOSA was a dominant PFAS detected in alaskan beluga whales between 1989-2006
24
Q

are contaminants transferred to offspring?

A
  • yes, PFAS has been found to be transferred from mother to fetus in marine mammals
  • transplacental transfer rates of PFCs were higher than those for PCBs and PDBEs
  • PFOS concentrations in harbour seal pups were 2.6-fold higher than those in adult females, suggesting the importance of maternal transfer
  • PFC concentrations in female bottlenose dolphins that haven’t been observed with calves were greater than those with calves, suggesting an off-loading effect
  • PFCs were detected in milk samples, confirming transfer of PFCs through lactation
25
what is the metabolic capacity to transform and eliminate PFAS?
- differs across species - analyses of PFOS:FOSA ratios indicated lower capacities to degrade FOSA in cetaceans compared to pinnipeds and polar bears - in vitro assays using liver microsomes showed that polar bears and ringed seals can rapidly transform N-EtFOSA to FOSA, whereas beluga whales lack the enzymatic ability or have a rate too slow to deplete levels of this precursor
26
PFAS and bottlenose dolphins in charleston:
- generalist feeding behaviour, long lived top level predator, high site fidelity to estuarine areas - some of the highest PFASs found globally in marine mammals have been observed in bottlenose dolphins in Charleston - plasma levels were comparable to those of occupationally exposed humans - five PCFAs and three PFSAs were detected - 13-fold greater concentrations than bermuda bottlenose dolphins
27
contaminants and Charleston harbour:
- local sediment samples were found to be higher than any other urban US area with over half of the sites exceeding median global PFOS sediment concentration - concentrations of PFOS and exposure to them may be greater in the water column than sediment
28
what are the contaminant sources in Charleston harbour?
- aquatic environments tend to be the primary sink in the environment for long chain PFASs - sources, both point and non-point, into the aqueous environment include: - industrial or municipal wastewater treatment plants - atmospheric deposition - landfill leachate - soil/street runoff
29
what are the health effects in charleston dolphins?
chronic exposures to high levels of PFASs in charleston dolphins were associated with: - immunity perturbations - altered liver enzymes - altered hematological parameters
30
what are 3 other marine mammal health-related effects?
- immunotoxicity - elevated PFOS and PFOA with diseased status in southern sea otter - altered thyroid hormone homeostasis in polar bears
31
what is still needed to respond to PFAS contamination?
- more data - there are no programs to meaningfully monitor the production, sources, fate, or transport of PFASs - better environmental monitoring programs must be implemented globally, across aquatic and terrestrial ecosystems - more research is needed on short chain PFASs: environmental concentrations and effects